Annals of Arid Zone-23(l), 55-62, 1984 Suspended material and solute concentration in flash flood water of Luni rher and its tributaries J. S. Central CHOUDHARI, K. D. SHARMA NND Arid Zone Research Institute, N. S. VANGANI Jodhpur-342 003 ABSTRACT Suspended material and chemical composition of the flood water of the Luni river and its tributaries draining an area of about 34, 866 km2 in arid part of western Rajasthan reveals that, suspended sediments were two to three times higher during flood (5830-13920 Cumec) than during low flows (495 to 1192 Cumec). Solute concentration show reverse trend because of dilution, to that of suspended sediment. Lithology of the area controls the sodium, potassium, calcium and mangnesium concentrations during flows. INTRODUCTION Occurrence of floods in desert streams especially in the Luni in Western Rajasthan is a rare event. Such an instance had occurred during July 1979 after a period of 117 years (Sharma et af., 1980) in the living memory. Along with a colossal amount of water, a mass of suspended and dissolved materials were transported rlownstream and thereby influenced physical and biological conditions in receiving systems. However, so far no data are available on transport characteristics of Luni and its tributaries during normal and flood flows. Therefore, the authors have tried in this paper to work out the water chemistry of high and low flows in the Luni and its tributaries during 1979 which will help in planning the water resource management in Indian desert. THE LUNI BASIN The Luni with its tributaries viz., . Jojari, Guhiya, Bandi, Sukri, Mitri, Jawai, Khari, Khari Bandi and Sagi forms the only integrated drainage system in the arid Western Rajasthan. It rises in the Aravalli hill ranges near Ajmer (260 27' N, 74° 39' E) and after an initial SWjW course towards Barmer flows SW until it drains into the NE corner of the Rann of Kutch (Fig. 1). This river system occasionally carry water generated in direct response to torrential rainfall during monsoon period and remains dry for rest of the year. The approximate basin area of the Luni is 34, 866 km2 (CAZRI, 1963) . The entire Luni basin is situated on hard rock and massive rock formations composed of volcanics, crystallines and 56 : et al. J. S. CHOUDHARI metamorphics, whereas the western part is covered with deep alluvium. All these formations occur at very shallow depths below alluvium and/or below sand cover varying from less than I m to over 40 m. Occurrence of CaCOa pan is a common characteristics of the terrain and is encountered at depths varying from 13 to I 12 em in river courses and 48 to 152 em in plains (CAZRI, 1963). MATERIAL AND METHODS Water samples were collected from 23 gauging stations (Fig. I) whenever the flow exceeded 45 em depth. These samples were transported to laboratory and filtered. Suspended material on filter paper dried, weighted and expressed in g/l. The filtrates were analysed for pH, conductivity, total sodium, potassium, sium, and are reported RESULTS AND dissolved calcium and solids, magne- in ppm. DISCUSSION The precipitation, flow characteristics and causes of the flash flood occurred in Luni basin during 1979 are reported by Sharma and Vangani (1982) and Sharma et al. (1982). The data on total suspended solids (TSS) in the Luni and its tributaries (Table I and Fig. 2) revealed that during the high flow (5830-13920 Cumec) period it was about 2 to 3 times than during tbe low flow (495- II 92 Cumec). Such high load concentrations are due to vulnerability of sparsely vegetated sandy and rocky slopes to erosion by heavy rainfall and flash runoff. The suspended load concentrations during flood (high flow) attained between 860 to 40,200 ppm which is quite in agreement with the 12,000 ppm in the water of Todd river at Alice springs in the Central Australian floods of 1967 and concentrations greater than 5,000 ppm are typical of floods throughout the arid western U.S. (Mabbutt, 1977). It increased sharply at downstream to Samdari and Gandav partly due to addition from different tributaries and mainly due to excavation and diminishing of flood discharge. The waters from all the streams are alkaline in nature and total dissolved solids (TDS) increased down-stream as the tributaries join the Luni (Fig. 3, Table 1). The solute concentration in various stream originating from the different lithology and geology revealed that spatial patterns of the TDS during the flood flows was much less than the low flows. This reduction during flooding was due to dilution. Similar distribution patterns have been reported for the Salt river, Kentucky (Hendrickson and Krieger, 1964), Salt river, Arizona (Rinne, 1975) and Sycamore Creek, Arizona (Fisher and Minckley, 1978). Further river Guhiya had contributed higher solutes than the other streams draining the various catchments. The presence of higher solutes in Bandi after PaJi was perhap due to effluent discharges from tbe dyeing industries is recorded at Jaitpur. and The concentrations of some selected cations revealed that by far all the waters 57 SOLUTES IN FLASH FLOOD WATERS ~o -;!. ••• ,. .. .. ..-:. or ••• .0 ~ ~i .,. ~~8 - , 0_ o.•...a: ? .... ..•.• " .. ,?i .. ;. .•~ ' .. ,', ~ VI r, :~~ _'4 .t .. " '", 0'; > , % U 58 : J. S. CHOUDHARI at. et Table 1. Suspended and solute concentration Streams catchment Station in high and low flows in Luni basin during 1979 TDS* (g/l) TSS** (gjl) High flow Luw flow High flow Low flow Mitri/Jojri Bisalpur 0.133 0.227 1.28 1.65 Luni Jasnagar 0.166 N.F. 0.86 N.F. Banjakuri 0.159 N.F. 4.65 N.F. Bilara 0.126 0.224 2.48 3.52 Samdari 0.544 0.860 14.88 1.98 Gandav 0.640 1.760 40.20 7.57 5.90 N.F. Sojat 0.063 N.F. Sheopura 0.066 N.F. 5.15 N.F. Singari 0.307 0.518 2.63 0.91 Soneimaji 0.307 N.F. 10.00 N.F. Pali 0.570 N.F. 11.40 N.F. Jetpur 0.218 1.529 11.31 7.57 Khari Bandi Madgaon 0.563 0.448 2.03 4.30 Sagi Sewari 0.256 N.F. 6.62 N.F. Guhiya Bandi Note - N. F. = No flow * TDS ** = Total dissolved solids. TSS = Total suspended solids. are sodium dominated except the waters from Jojri, Sagi and upper Luni catchments which have calcium as dominant cation (Figs. 4 and 5). Under high flow conditions about three fourth of the basin area drained waters containing 25 ppm sodium, whereas the waters from the same area under low flow conditions contain 100 - 300 ppm sodium. Similarly, the lower part of the basin which under the high flow conditions drained 50 ppm Na drained 300-500 ppm Na during the low flow conditions. Similar concentration patterns were observed for potassium ion also. Calcium (Fig. 5) being the next dominating cation, three fourth of the basin area drained 10-30 ppm Ca under high flow conditions drained 20-80 ppm l SOLUTES IN FLASH FLOOD WATERS rOTAL TOTAL SUSPENDED SOLIDS IN HIGH AND DISSOLVED SOLIDS 59 IN HIGH AND LOW FLOWS OF LUNI BASIN DURING· 1979 LO~ FLOWS OF LUNI BASIN DURING 1979 t~ I I I . 14 ~-I HIGH FLOW lOlAOf' LOW FLOW SC.••..•• Fig. 2. lolU HIGH FLOW Cl.A IY CRQ,(lc"a~I"'L.oII .•• ~"""O<..,._".•• c ••• ·...,_ Total suspended solids in Luni basin during 1979. . under the low flow conditions. Magnesium content has shown a different pattern than the above three cations (Fig. 5). Half of the: basin!draining eastern part fjhave 3-6 ppm Mg under high flow conditions, drained 3-9 ppm under the low flows. The remaining half, lower part which was draining 6 ppm Mg under high f1ow:conditions drained 15-21 ppm during the low flows. In terms of the above dissolved sub~tances, floods are often viewed as dilution CIACLE.!C.,.l:-: SC~E e LOW FLOw ..fTO'S,i'a/Lrt! .,/L.t .t.· •••,'-o..OC'l_'Qh t .O~••h. Fig. 3. Total dissolved solids in Luni basin during 1979. phenomena in which low conductivity rain water dilutes ground water that are nearer chemical equilibrium with substrata and thus rich in dissolved saIts. Therefore low concentrations under high flow conditions are observed. This dilution effect is partially offset by leaching and dissolution of sol utes from newly exposed rock and soil minerals as well as from the suspended particles and thus higher concentrations are observed under subsequent low flows. Similar _ 60 1. S. CHOUDHAR I et af. R f -·ee ee -B.o. --o ~z~ 0.0. 0.0. 0.0. C ~Z~ o I~ o ..J. II u. I I it .•.i : J: ! t c> , I X I I ~l 0' -1: ell c: .~ .~ Q Q . •.. •~ 9 SOLUTES IN FLASH FLOOD WAT ERS ~ .~ I -e IE 0. 0.. 0.0. a:r ~ ...J f • u. , J: J ~ J..J ILL ~ I ~J Ce 0.0. _ o.a. 8~ '~ ! I I Q I 'O~ :t i J..:.J , I . '~ '!l 11 '0 ~. I \ : 61 62 : J. S. CHOUDHARJ et al. results were also reported by Johnson and Needham (1966), Hem (1967) and Fisher and Minck1ey (1978). The variation in total dissolved substances and cations amongst the various catchments is mainly due to the lithology of the area. Eastern part of the basin which is dominated by schist, gneiss and calc-schist and slow weathering environment yielded, less salts than the lower half of the basin, which is covered by alluvium, have salts on the surf.lces due to high temperature are added to the runoff in the rainy season. Rodda et al (1976) reported lithological control on solute concentrations to greater extent than the other factors. ACKNOWLEDGEMENTS We are grateful to Dr H. S. Mann and Dr. K. A. Shankarnarayan, Director and Head of Division, respectely, CAZRI, Jodhpur, for facilities and encouragement during the study. REFERENCES Hem, J. D. 1967. Study and interpretation of the chemical characteristics of natural waters. U. S. Geological survey, water supply paper 1473: 1363. Hendrickson, G. E. and Krieger, R. A. 1964. Geochemistry of the natural waters of the Blue grass region, Kentucky. U S. Geological survey, lVater supply paper 1700: 1-135. Johnson, C. M. and Needham, P. R. 1966. Ionic composition of Sagehen creek, California, following an adjacent fire. Ecology 47: 636-639. Mabbutt, J. A. 1977. Desert Ilandforms. Australian National University Press, Canberra. Rinne, J. N. 1975. Hydrology of the Salt river and its reservoirs, central Arizona. Arizona Academy of Sciences 10: 75-86. Rodda, J. c., Dowing, R. A. and Law, F. M. 1976. Systematic Hydrology. Newnes-Butterworth, London. Sharma, K. D. and Vangani, N. S. 1982. Some rainfall festures of July 1979 storm over Luni Basin Ann. Arid Zone 21 (I): 22-32. CAZRI I1J63. Basic resources of Central Luni basin, Western Rajasthan. Divisonal report No. 63/1. Fisher, S. G. and Minckley, W. L. 1978. Chemical characteristics of a desert stream in flash flood. J. Arid Environ. 1: 25-33. Sharma, K. D., Vangani, N. S., Chatterji, P. C. and Ganga Singh 1982. U nprecendented floods in Lun i basin, Western Rajasthan during July 1979-A case study. Mal/sam 33(3): 377-384.
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